Title: Chapter 6 Atmospheric Aerosols
1Chapter 6Atmospheric Aerosols
2Atmospheric Aerosols
- Solids in gas
- Dust, smoke, fly ash, pollen
- Liquids in gas
- Cloud, mist, fog, smog
3- Particles can scatter light if they are the same
size as the wavelength of light
4- Large particles settle quickly
- Small particles stay suspended
- Very small particles coagulate
- PM10 particles less than 10 mm
- PM2.5 particles less than 2.5 mm
5Breathing particles
- PM10 particles are not removed when breathing
through the nose - Particles can enter lungs
- PM2.5 particles pose more of a health threat
- Particles contribute to breathing problems
6Ways of measuring particles
- Coefficient of haze (COH)
- 300 linear meters of air are drawn through filter
and the absorbance of the filter is measured - COH 100 times absorbance
- COH gt 6 indicates air that will cause severe
respiratory problems - Total suspended particulate (TSP)
- Gravimetrically measure quantity of particulates
by filtering air at a rate of 1.4 m3/hr - 10-30 mg/m3 common, but 500 mg/m3 has been
observed in Toronto - Total dustfall (TSF)
- Passively weigh dust that settles into an open
topped container over 30 day period - gt 7.0 g/m2/month considered excessive and is
commonly found in highly industrialized areas
7Ways of measuring particles
- Inhalable particulates (IP)
- Course (2.5 10 mm) to fine (lt 2.5 mm)
- Measure with an impactor
- Can make small models to be carried with people
to measure their exposure to particles
8Sources of particles
- Natural and anthropogenic sources
9Sea spray aerosols
- Small droplets 5 25 mm contain 2 -200 pg salt
- Small enough to stay in air
- Large droplets 25 500 mm contain 200 pg to 2 mg
salt - Fall back to water
- Sea surface microlayer is often different
composition than bulk water - Polar-nonpolar interface
- Aerosols may be enriched in nonpolar molecules
compared to that predicted by bulk water
10Dust
- Rural dust
- Soil components
- Desert dust storms
- Agricultural lands
- Urban dust
- Cement particles
- Tire particles
- Brake lining particles
- Solid aerosols from vehicle exhaust
11Combustion products
- Carbon fuel gt fuel rich conditions gt black
smoke - Common in diesel engines
- White smoke gt condensed water vapor
- Coal combustion
- Fly ash
- Bottom ash
- Bottom ash from university power plant is used
for road traction in Cape County
12Polycyclic Aromatic Hydrocarbons (PAHs)
- Formed during incomplete combustion of wood,
coal, liquid fuels, meat, charcoal - 150 compounds 2-8 rings
- Hamilton Ontario 10 ng/m3 in summer and 30 ng/m3
in winter - 80 of PAHs associated with soot particles less
than 3.3 mm.
13Condensation aerosols - sulfate
- Sulfur compounds in -2 oxidation state are
oxidized to sulfuric acid (Chapter 5) - COS, H2S, CS2 etc
- Ammonia is released during microbial breakdown of
organic matter - Ammonia and sulfuric acid react to form solid
particles (0.1 1 mm) - Water condenses on these particles
NH3 H2SO4 ? NH4HSO4 2NH3 H2SO4 ? (NH4)2SO4
14Condensation aerosols - organic
- Terpenes emitted by trees cause condensation
aerosols similar to those formed in photochemical
smog events - a-pinene is produced by pine, spruce, and fir
trees - 0.1 50 ppbv in forest air
- Isoprene is produced by willow, oak, poplar, and
aspen - 1 10 ppbv in forest air
15Condensation aerosols - organic
- Terpenes are oxidized to aldehydes, ketones, and
carboxylic acids which condense to form small
particles (lt 0.3 mm) - Photochemical haze over forests (Great Smokey
Mountains, NC) - Aerosol production from forests 20 Tg/yr
16Aerosol concentrations
- mg/m3 rather than mol/m3
- Lower concentration of aerosols than trace gases
- CH4 1200 mg/m3
17Aerosol lifetimes - Settling
- Settling velocity due to gravity (Stokes Law) is
dependent on - Density of particle (rp)
- Density of air (ra)
- Stokes-Cunningham slip correction (C)
- Acceleration due to gravity (g)
- Particle diameter (dp)
- Viscosity of air (?)
18Aerosol lifetimes Settling 10 mm particle
- Settling due to gravity is in competition with
air currents lifting the particle
19Settling velocity
- gt10 mm considered settleable
- lt10 mm remain suspended due to upward movement of
air
20Aerosol lifetimes - Coagulation
- Brownian diffusion of small particles to form
larger particles dependent on - Particle concentration (N)
- Diffusion coefficient of the particles in air (D)
- Stokes-Cunningham slip correction (C)
- Particle diameter (dp)
21Aerosol lifetimes Coagulation 0.01 mm particle
- Brownian diffusion of small particles to form
larger particles dependent on - Particle concentration (N)
- Diffusion coefficient of the particles in air (D)
- Stokes-Cunningham slip correction (C)
- Particle diameter (dp)
22Coagulation
- gt 0.1 mm coagulation not important
- lt 0.1 mm coagulation will occur removing this
size of particle
23Residence time of particles in atmosphere
- Large particles have short residence times due to
settling - Small particles have short residence times due to
coagulation - Particles in the 0.1 100 mm range have longest
residence times
24Control of anthropogenic point sources of
particles
- Cant control sources like volcanoes and sea
spray - Can prevent forest fires
- Settling chamber
- Baffles and open spaces designed to allow the
particles time to settle before being released
25Control of anthropogenic point sources of
particles
- Cyclones
- Cone-shaped device causing waste stream to swirl
rapidly - Large particles collide with wall due to
centrifugal force
26Control of anthropogenic point sources of
particles
- Filter
- Waste stream passes through a porous filter
similar to a vacuum cleaner - Small particles plug the pores
27Control of anthropogenic point sources of
particles
- Scrubbers
- Fine mist of water to add water to particles
- Larger particles are easier to remove by settling
28Control of anthropogenic point sources of
particles
- Electrostatic precipitator
- Particles in waste stream become charge when
passing in areas of electron flow between two
electrodes - Charged particles move toward positive electrode
and are removed
29Summary of control of anthropogenic particles